The Public Good Nature of the Urban Forest and Implications for Management

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The Public Good Nature of the Urban Forest and Implications for Management DRAFT The Public Good Nature of the Urban Forest and Implications for Management Shannon Lea Watkins School of Public and Environmental Affairs Center for the Study of Institutions, Population and Environmental Change April 8, 2015 Vincent and Elinor Ostrom Workshop in Political Theory and Policy Analysis, Indiana University, Bloomington, IN Abstract: This paper uses the context of the urban forest to illustrate how identifying the nature of goods yields important implications for the management of natural resources. Urban trees provide an array of economic, social and environmental benefits, yet canopy cover in cities in the United States is frequently lower than desired and often decreasing. Given the public benefits of urban trees, some scholars have referred to urban trees as a public good. However, little work has given the discussion more than a few sentences and scholars disagree over the “nature of the good” for urban trees. Even less work has connected the public goods nature of the urban forest to the challenges of urban forest management or used it to inform evaluation of policy tools for urban forest management. This paper lays out the argument that the urban forest is best considered as a public good, rather than as a common pool resource. It then illustrates the implications of this argument for the health of the urban forest—without public intervention, there are fewer urban trees than is socially optimal. Finally, it discusses the implications of this argument for urban forest management, including a discussion of policy tools most suited to encourage tree planting and care. It concludes that two options offer opportunities to increase both public and private trees: grants to and coproduction with residents in planting and maintenance activities. 1 DRAFT 1.0 INTRODUCTION Urban trees provide an array of local and global benefits (i.e. ecosystem services), including benefits to the environment, to public health and to communities. Yet, urban forests have declined in many cities in the last few decades and urban canopy cover in many cities is below recommendations or targets (Nowak & Greenfield, 2012). Properly identifying “the nature of a good” is important to selecting appropriate strategies to address environmental problems (Gibson et al. 2000). Previous work in urban forestry has briefly mentioned the nature of the good (e.g., see Mincey et al. 2013), but there is disagreement among scholars whether components of the urban forest are public goods or common pool resources. Additionally, little work has given the discussion more than a few sentences (see Fischer & Steed 2008 for an exception). Even less work has connected the public goods nature of the urban forest to the challenges of urban forest management or used it to inform evaluation of policy tools for urban forest management. This paper lays out a more thorough treatment of the “nature of the good” question and demonstrate how an understanding of the nature of the good can inform management. Along the way, it seeks to clarify concepts and terms that have been inconsistently used in the literature and considers the extent to which we can draw on previous research in rural forests to understand management in urban forests. By examining the kinds of ecosystem services that urban forests provide (discussed in this introduction), Section 2.0 argues that the urban forest is best considered as a multi-faceted public good. The paper then draws some implications of this argument for the structure and function of the urban forest in Section 3.0—without public intervention, there are fewer urban trees than is socially optimal. Cities across the United States vary dramatically to the extent and manner in which they manage and regulate the urban forest (Profous & Loeb, 1990). Section 4.0 discusses policy tools for urban forest management and comment on their suitability in light of the discussion in section 3.0 and of the particular characteristics of the urban forest. 2 DRAFT Defining the urban forest Before tackling the “nature of the good,” this section defines the urban forest and its components. Tyrväinen and Väänänen consider the urban forest “wooded areas located within town limits or close to town” (Tyrväinen & Väänänen, 1998, p. 117). Their definition includes forested parks, recreation areas and protected forests but explicitly excludes constructed parks (Tyrväinen & Väänänen, 1998) and also seems to exclude trees near streets and in yards. Strom (2007, p. 99) offers a more inclusive definition of the urban forest: “the land in and around areas of intensive human influence, ranging from communities to dense urban centers, which is occupied or potentially occupied by trees and associated natural resources.” His definition includes land that is “planted or unplanted, used or unused, and includes public and private property and street, transportation and utility corridors” (Strom, 2007, p. 99). While Strom praises his definition for including potential future urban forests, this paper is concerned with the presence (and absence) of actual trees. The difference between planted and potentially planted land is significant. This paper considers the urban forest to be the land in and around areas of intensive human influence which is occupied by trees and associated natural resources. Frequently it refers to urban trees, the trees that are part of the urban forest. Urban trees grow in a number of different urban land areas, including in parks and recreation areas; near waterways and other natural features; in remnant forests; in brownfields and abandoned properties; in private yards, and in public rights of way along streets. Strom (2007) argues that the distribution of the urban forest between private and public land dictates the kind of policy that will effectively protect and improve urban forest structure and function. Much early urban forestry research focused on street trees and to a lesser extent, park trees (Loeb, 1987). An estimated 90% of urban trees are on private land on average (Gerhold, 2007), and recent research has considered policy related to these trees (Donovan & Butry, 2010). Noting the ecological importance of trees on both types of land, and noting the policy importance of distinguishing between these types of trees, this paper focuses on both “public trees” (trees growing on public land) and “private trees” (trees growing on private land)— collectively, urban trees. There is no consensus on the definition of street trees so this paper 3 DRAFT adopts a general definition used elsewhere (see Fischer and Steed 2008) and defines street trees to be those trees in cities that are located in close proximity to public streets. Street trees then, although commonly planted on public property, might be private or public trees. The benefits and costs of urban trees Benefits. Urban trees provide environmental, economic, health and social benefits (Peper, McPherson, Simpson, Vargas, & Xiao, 2009) at a number of scales. Trees can improve the local urban environment. They can filter particulate matter and other air pollutants to improve local air quality (Nowak 2006). They can intercept rain and help to reduce local flooding and can improve local water quality (Xiao, Mcpherson, Ustin, Grismer, & Simpson, 2000). Trees can also yield local economic benefits. Strategically planted trees can reduce cooling costs in summer by shading homes and reduce heating costs in winter by blocking cold winds (McPherson & Simpson, 2003). Trees have also been found to increase economic activity in urban business districts (Wolf, 2003), and to raise the value of both properties on which they are planted and of neighboring properties (Donovan & Butry, 2010). Urban trees have been found to improve health and well-being of individuals nearby. One of the most often cited values of urban trees is their contributions to city appearance (aesthetic benefits). Trees can also benefit public health. For example, trees were found to reduce mental fatigue and to increase ability to cope with critical issues for poor residents in urban public housing (Kuo, 2001); to reduce levels of stress in deprived communities (Ward Thompson et al., 2012); and to hasten recovery time of hospital patients (Ulrich, 1984). Trees can also serve architectural and design functions like acting as a screen to block an unsightly view (Ingram, 2007; Lawrence, 1995). At the city or regional level, trees provide significant environmental benefits, particularly in reducing urban temperatures and mitigating the urban heat island effect (Rosenzweig et al., 2006). Globally, urban trees also serve as a sink for atmospheric carbon dioxide, and so contribute to climate change mitigation (Nowak & Crane, 2002). 4 DRAFT Benefits of trees as ecosystem services. Some scholars refer to the benefits of urban trees and other environmental amenities as ecosystem services—“the benefits people obtain from ecosystems” (Mincey et al. 2013, Millenium Ecosystem Assessment, 2005 p. v). There are four primary types of ecosystem services: provisioning services (e.g. food, timber, water); regulating (e.g. climate regulation, water purification); supporting (e.g. nutrient cycling, photosynthesis), and cultural services (e.g. recreation, spiritual experience) (Millenium Ecosystem Assessment, 2005). If we characterize the benefits of urban trees according to this typology of ecosystem services, a clear pattern emerges. Although some urban trees provide food (i.e. fruit trees), and a few urban trees might be harvested for timber (or, for
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